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1 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
Sustainability of Three Recreational Forest Landscape
Management in Selangor, Malaysia
Mohd Kher Hussein12 1Department of Landscape Architecture, Faculty of Design and Architecture, Universiti Putra Malaysia,
Serdang, Selangor, Malaysia. 2Faculty of Landscape Architecture, Corvinus University of Budapest, Villanyi ut 35-43. P.O.B. 53. H-
1118 Budapest, Hungary.
[email protected]/ [email protected]
Different stakeholders managed recreational forests in Selangor, Malaysia. These
stakeholders’ involvements have risen a question whether their development have fulfilled the
sustainable landscape requirement. The aim of this study was to understand and generate more
comprehensive knowledge on the recreational forest landscape management towards forest
sustainability. The objectives of this study were to evaluate the management of recreational
forest in Selangor, Malaysia that affect landscape sustainability and to gain an overview of
recreational forest landscape development in Peninsular Malaysia. The study applies three
methods. First is the analysis of documents relating to sustainable landscape concept.
Secondly, through case studies where three recreational forest sites in Selangor were selected
to analyze their management practices towards landscape sustainability. Thirdly, field
observations were carried out to collect data about existing physical conditions of the study
sites. The results revealed that landscape management of these recreational forests were not in
accordance with landscape sustainability approaches and needs improvement. This was caused
by improper planning, low understanding among the staffs regarding sustainable landscape
management, shortage of knowledgeable personnel, and poor supervision. Failure to adopt and
implement sustainable landscape practices which include environment protection, social
improvements, good governance, aesthetics enhancement, economy benefits, and harmonized
designs can lead to the increase in the “abandon syndrome” of some recreational forest sites in
Peninsular Malaysia.
Keywords: sustainable landscape management, landscape architecture, landscape
management, recreational forest.
1. INTRODUCTION
From a landscape perspective, sustainable
landscape refers to the role of landscape in
sustainable development and to the sustainable
protection, management, and/or planning of
landscapes (Selman, 2008). In landscape
architecture and planning, there is a professional
subculture that interprets sustainability in terms
of low-impact design (Dunnett & Clayden 2007).
Selman (2008) divides sustainable landscape into
two aspects. First is the design and scenic assets
protection and second, the relationship between
ecosystem services and human well-being. This
means that in sustainable landscape development
there is a need to focus on restoration,
preservation, conservation, protection of natural
systems, maintaining natural function and
environmental quality in developing a forest area
(Schutzki & Tripp, 2007).
Sustainable landscape development also
requires reconciling society’s development goals
with the capacities of landscape systems to
deliver ecosystem services over long-term (Clark
& Dickson, 2003; Kates et al., 2001; NRC,
1999). Landscape systems are complex,
adaptive, and tightly coupled social-ecological
systems (GLP, 2005). Therefore, continuously
sustainable states of landscapes are unlikely and
efforts for supporting sustainable landscape
development should always aim at making
progress on a transition towards sustainability
(NRC, 1999).Sustainable landscape development
is generally considered right at the inter-section
of environment, economy, and society. It is also
2 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
further influenced by two other dimensions
which are governance and aesthetic sustainability
(Selman, 2008).
There are six factors affecting landscape
sustainability of recreational forests. The first
one deals with landscape ecology of spatial
patterns and processes (Farina, 2006; Selman,
2008). This is commonly referred to as the
green infrastructure which involves biodiversity
network of habitat patches and corridors in
maintaining healthy and practical populations
(Selman, 2008). It also refers to soil and nutrient
conservation, water quality, hydrology systems
and vegetation’s (Haines-Young et al., 2006). A
proper recreational forest landscape planning
(especially in terms of human made landscape
elements) is necessary because landscape is an
ecological entity that is dynamic and changes
according to situation and disturbance (Ismail &
Mohd Sarofil, 2005). Human activities
frequently cause impact to the environment
causing resulting environmental destruction and
creating unhealthy environment to living things.
Secondly, sustainable recreational forest
landscape relates to the economy. This relates to
benefits such as recreational activities that makes
certain places interesting and haves values to the
public (Powell et al., 2002; Selman 2008; Vollet
et al., 2008). Those economic benefits should
also bring benefits to local people to improve
their quality of life. Furthermore, Jamieson and
Noble (2000) claimed that recreational forest
development should provide job opportunity,
reducing poverty and cut social inequality and
increase social services to the local community.
Thus, a proper and systematic recreational forest
landscape development needs to take into
account local community economic enhancement
to make sure the sustainable use of recreational
forest.
Thirdly, sustainable recreational forest
landscape is also related to the needs of local
populations. For generations, parks including
recreational forests have played important roles
for people, and contributed to social and cultural
aspects of their lives (Osman, 2005; Nicol &
Blake, 2000). Parks also provide a powerful
setting for “social” (Collins et al., 2007) and
“sustainability” learning (Tabara & Pahl-Wostl
2007). Thus, local participation in recreational
forest landscape plans and design process is
necessary. This is to ensure their requirements
are met and to avoid injustice in decision-making
as well as to get their full support (Botes &
Rensburg, 2000). Buchecker et al. (2003) argued
that local participation exercises in planning and
landscape design process of recreational forest
landscape need to be improved to increase their
understanding on landscape sustainability.
Unfortunately, in Malaysia, there are still many
local participation exercises that do not take into
account people’s real opinions and their needs.
This is because when authority organized local
participatory exercises, it only involves the
authority giving information to the public but not
really getting any real feedback from them
(Ahmad, 2001 as cited in Mohd Yazid, 2009).
A fourth factor is good governance. This is
closely related with political sustainability and
requires effective governance structures, for both
the private and public domains (Selman, 2008).
Good governance also requires a stable
governance to ensure that landscape
development requirements are being
implemented according to the strategy with high
integrity and intentness (Hamilton & Selman,
2005). Good governance is important at all levels
i.e., from international to local levels. However,
it is particularly important at the local level,
where numerous high-level decisions can be
implemented, ignored or even contradicted
(Rametsteiner 2007). Szerletics (2011)
highlighted the characteristic of good governance
as follows:
(1) Transparency – decisions taken and
their enforcement are done in a manner
that follows rules and regulations. It
also means that information is freely
available and directly accessible to
those who will be affected by such
decisions and their enforcement.
(2) Responsibility and accountability – the
decision-makers in the government,
private sector and civil society are
accountable to the public and/or to their
institutional stakeholders.
(3) Participation – the public can
participate (either directly or through
representatives) in the decision-making
and the implementation of public
projects or other government activities.
(4) Responsiveness to the needs of people –
good governance requires that
institutions try to serve all stakeholders
within a reasonable timeframe.
(5) Effectiveness – processes and
institutions produce results that meet the
3 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
needs of society while making the best
use of resources at their disposal.
(6) Equity and inclusiveness – this principle
requires that all groups, but particularly
the most vulnerable, have opportunities
to improve or maintain their well-being.
(7) Rule of law – this principle requires fair
legal frameworks that are enforced
impartially.
(8) Consensus oriented – good governance
requires mediation of the different
interests in society to reach consensus.
Clearly, good governance of recreational
forest needs transparency, accountability,
regulatory reform, skills, cooperation, leadership
and public participation in their implementation
process. The author believes that good
governance actually is very important in creating
a responsible and conducive recreational forest
environment. This is especially in their
implementation and management.
The fifth factor is related to landscape
aesthetic values. Aesthetic value has influence
people to react towards recreational forest
landscapes based on their experiences in
proximity of the landscape (Gobster et al., 2007).
This is because people try to value or perceive
recreational forest landscape through aesthetical
values such as to what they observe and to how
the landscape is being managed. Selman (2008)
claim that landscapes have varying degrees of
legibility that betray underlying narratives and
the extent to which we appreciate or denigrate a
landscape is closely related to the way people are
taught to “read” it. Apart from that, landscape
aesthetic also has a close relationship with
ecology that gives impact to planning, design
and management of natural sites (Gobster et al.,
2007). An exploration on how people appreciate
recreational forest landscape could be explored
to understand how people aesthetically value
landscapes (Gobster, 2008).
The sixth recreational forest landscape
sustainability factor is the design aspect. The
design of sustainable recreational forests must be
in harmony with natural forest landscapes. It
should take into account their own unique
features that highlight the forest identity and act
as a tourism product besides being sites of
recreational activities (Jacobs, 1993). The design
also must have good combinations between the
natural environment and architectural aspects
such as application of vernacular architecture
(Schmid, 1983). Design of hardscape structures
(e.g. pedestrian path, signage, shelter, etc.) as
well as buildings, must be visually in harmony
with the surrounding natural environment
(Schneider, 1981). Forests with high
panoramic values should have buildings with
good style that is in harmony and did not
contradict the existing environment (Doczi,
1994). Design of buildings and other structures
should depend on climate, temperature, light and
color (Stouter, 2008). These factors must be
seriously considered during the design process.
Ceballos-Lascurain (1996) and Walter (1987)
suggested that the most important consideration
is that the structure and building designs in
recreational forest must highlight aspects of the
surroundings.
2. AIM AND OBJECTIVES OF THE
STUDY
The aim of this study was to understand and
generate more comprehensive knowledge on the
recreational forest landscape management
towards forest sustainability. The objectives of
this study are to evaluate the recreational forest
management in Selangor, Malaysia that affect
landscape sustainability and to gain an overview
of recreational forest landscape development in
Peninsular Malaysia.
3. METHODOLOGY
This study applied three methods. The first is the
document analysis of relevant literature where
the author analyzed the topic of sustainable
landscape concept to understand the topic and to
find out what has been done by other researchers
on recreational forest landscape sustainability.
Peer-reviewed literature and best practice
guidelines were also included in the study. Even
though the best practice in sustainable landscape
does not appear in peer-reviewed journals, they
are based on experiences and practical
knowledge of the experts in forest park
management that is being considered important.
Secondly, the study involved a case study
where three recreational forest sites in Selangor
State, Malaysia were selected. These were
Sungai Tekala Recreational Forest, Sungai
Chongkak Recreational Forest and Templer
Recreational Forest. Case studies were used in
this study because this method is applicable to
real-life, contemporary, human situations. Case
study results also relate directly to the common
4 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
reader’s everyday experiences and make easy to
understanding the complex real-life situations
(Soy, 1997).
Thirdly, field observations were carried out
to collect data about existing physical condition
of the study sites. Field observations were
carried out in detail, free from bias, and care was
taken to ensure the information gathered were
original and reliable (Lee, 1976; Mohd Kher,
2012). Photographs were taken during field
observations as evidences of visual assessment
regarding current status of landscape
management works on the study sites.
Recreational forests in Selangor were
selected for this study because Selangor is the
fastest developed states in Malaysia and forest
recreations have a high demand from the public.
The rate of urbanization in this State is expected
to increase significantly mainly due to migration
of people from surrounding states, as well as the
influx of foreign workforce. This has resulted in
conflicts between urbanization and forest
reserve. Moreover, Selangor has the highest
population in the Klang Valley that has put
pressure to their forest as well as recreational
forest for land use (e.g. housing development
and industrialization). This presents a challenge
for recreational forest landscape development
and management strategy in ensuring their forest
are not affected by those development and being
managed in a sustainable way. Selected study
sites are also easily accessible by the public and
this posed challenges to the forest authority
name the Selangor Forest Department seeking to
improve the landscape including existing
facilities.
4. RESULTS AND DISCUSSION
Currently, there are ten (10) recreational forest
sites in Selangor managed by different
stakeholders: Selangor Forestry Department
(SFD), Selayang Municipal Council (MPS) and
Tourism Selangor Sendirian Berhad (TSSB)
(Table 1). Different stakeholders involvement
have resulted to more development focused been
given on getting revenue and profits for
managing the site. SFD and MPS are the
stakeholders that have motivated towards
conservation, while TSSB seemingly geared to
profit stakeholder. Indirectly, this phenomenon is
not in line with the main goal for recreational
forest establishment to increase awareness
among the public towards forest functions in
daily life and sustainable use of natural forest
resources in Malaysia.
In general, the three study sites have very
similar characteristics in terms of accessibility,
layout, and man-made elements, particularly the
buildings. However, each study site has their
own uniqueness and there are being determined
by their topography, either hilly or otherwise,
waterfall and history. Two of the study sites are
generally well-preserved in terms of forest
originality. Templer Recreational Forest,
however, is under threat due to rapid
development in the surrounding areas such as
housing development, road constructions and
golf course.
Table 1: Recreational Forest in State of Selangor,
Malaysia
Recreational Forest Manage
By
Gunung Nuang, Hulu Langat SFD
Sungai Tekala, Hulu Langat SFD
Sungai Tua, Ulu Yam SFD
Sungai Chongkak , Hulu
Langat
TSSB
Sungai Sendat, Rawang SFD
Kanching, Rawang TSSB
Templer , Rawang MPS
Ampang SFD
Komanwel SFD
Hulu Perdil SFD
(Source: Forestry Department Peninsular
Malaysia 2007)
4.1 SUNGAI TEKALA RECREATIONAL
FOREST
Sungai Tekala Recreational Forest is located in
Hulu Langat district (coordinates 03o 03'62 "N
101o 52'13" E). This park is part of the Sungai
Lalang Forest Reserve consisting of lowland
Dipterocarp Forest type. The Selangor Forestry
Department (SFD) developed this park in 1982
and it was opened to the public in the same year.
This recreational area is approximately 2,062
hectares. SFD still managed this area until today.
This park is intended to be developed as a
recreational area and for environmental
educational purposes. The park charges an
entrance fee of MYR1 (USD 30 cents) for adults
and MYR0.50 (USD 15 cents) for children 12
years and below.
5 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
From an ecological aspect, its sustainability
is being threatened because the landscape
development of this site was implemented
without a proper landscape master plan. The
development was carried out on an ad hoc and in
situ basis depending on visitors suggestions of
what facilities were required by them. Others
were provided by the Department regardless of
whether they were actually needed or not, or
whether they were suitable for the locations and
have adverse impacts on the surrounding forests.
Failure of the management to control the number
at one point in time has caused overuse of the
forest park and led to soil compaction impacting
existing vegetation. Urgent solutions need to be
carried out by the management to ensure future
park ecological sustainability.
It was also observed that facilities were not
designed in harmony with the surrounding
environment and lacks the forest identity. Most
of their designs seem to be similar to those of
urban parks (Figure 1). If this continues, it can
result in failure to achieve its sustainable
development goal. In terms of architectural
designs, it portrays local traditional Malay
architecture (Figure 2). This is evidenced in the
typical roof design and materials used (wood and
clay bricks). The color schemes chosen are those
of green and chocolate inducing “cool” and
“peaceful” response in visitors (Brenda &
Robert, 1996). Those colors are suitable for
forest environment and can influence user
comfort (Arwed 1992). Enhancing local
indigenous design, materials and natural colors is
a good step taken to indicate local environmental
influences (Ceballos-Lascurain 1996; Walter
1987).
Figure 1: Some of the forest recreation designs similar to urban park designs in Sungai Tekala Recreational
Forest.
Figure 2: Enhancing Malay architecture to show local culture and in line with ecotourism concept.
Figure 3: Poor maintenance causing damaged and unusable structures and equipment in Sungai Tekala
Recreational Forest.
6 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
The management paid special attention to
site cleanliness such as regular rubbish
collection, sweeping dry/fallen leafs along
pathways, toilets cleaning and waste disposal.
However, maintenance work for human made
landscape elements such as shelters, benches,
rubbish bins, bridges, signage and pergola, were
not promptly carried out whenever required.
This attitude has resulted in some structures and
equipment seriously damaged, unusable and
affecting the park aesthetic values (Figure 3).
Therefore, it is necessary for the management to
prepare and set up proper maintenance plan and
schedules to fulfil sustainable concept enhancing
the aesthetic value to users. This is very
important to ensure their quality experiences
were not degraded and they have positive
reactions towards the site when using the park.
There is very little local participation in the
management of Sungai Tekala Recreational
Forest management. Local people were not
involved in the management process such as in
discussing the future direction of park
development. They were also not consulted to
determine recreation activities and choice of
facilities and equipments. Therefore, the
management should be more proactive in finding
ways to increase community involvement in park
planning development and activities. This could
be done through “homestay”, “agro tourism” and
cultural activities. It is recommended that local
community representatives be appointed to allow
them to be involved in the development process
through Recreational Forest Development
Committee. These involvements would increase
their ability to give ideas, opinions, better
cooperation and commitment in conserving
recreational forest in their area. This can lead to
the achievement of landscape sustainability of
recreational forest objectives.
In terms of governance, Sungai Tekala
Recreational Forest has relatively good
governance by the Selangor State Forestry
Department (SFD). SFD has sufficient foresters
who are excellent in forest management.
However, the department lacks expertise in site
selection, planning, management as well as
technical expertise in preparing and
implementing a systematic working plan of
landscape design, construction and management
(Chee, 1986, Mohd Kher, 2012). This lack of
expertise has resulted in deficiency of eco-design
approach for human made landscape elements
such as bridges, shelters, toilets and other
facilities. It is recommended that the
management appoint a qualified landscape
person including landscape technicians
competent in built environment design and
management. At the same time, the management
needs to establish a unit specifically overseeing
recreational forest development. The unit should
consists of forester, landscape architect,
engineer, ecologist and architect.
From the economic aspect, the park
management allowed the participation of local
community where they are allowed to run a
small businesses catering to visitors outside the
park boundary. This has helped locals to
improve their economy by selling fruits, drinks,
handcrafts, and other agriculture produce (e.g.
durians’, petai, mangostane, bananas and
mangoes). Nevertheless, locals are not much
involved in recreation/tourism related
employment (e.g. as park ranger/park controller).
Thus, the management needs to increase
opportunities where local youths can be trained
to work various jobs in the park.
4.2 SUNGAI CHONGKAK
RECREATIONAL FOREST
Sungai Chongkak Recreational Forest is located
in Hulu Langat district (coordinates 03° 12'41"
N, 101° 50'27" E). This area covers
approximately 2,865 hectares of lowland
Dipterocarp Forest types and is part of the
Sungai Lalang Forest Reserve. The Selangor
State Forestry Department developed this park in
1992. Beginning in January 2005, SFD handed
over the management of this site to the Tourism
Selangor Sdn. Bhd. (TSSB). This was done due
to shortage of manpower, increase in costs of
maintenance and insufficient budget. Since
TSSB took over the park, ecotourism concept
with sub-concept of ‘resort’ had been
implemented in 2005. TSSB applied ecotourism
concept with “resort” as sub-concept to
encourage families or other groups to participate
in their recreational activities. TSSB also aimed
to attract foreign tourists by offering
conveniences and providing international
standard accommodation facilities. Thus, the
park has now been turned to tourist destination
and charged entrance fees of MYR1 for adults
but free for children aged 12 and below.
From an ecological perspective, the Sungai
Chongkak Recreational Forest faces threat due to
lack of a comprehensive plan being developed by
7 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
the management. Currently, TSSB only applied
the development ad hoc approach where the
development was based on users’ requests. This
approach is unsuitable and has resulted in
environment degradation such as soil erosion,
flora and fauna destruction, and visual quality
reduction (Figure 4).
However, Mustaqim-Alias & Ahmad (2013)
claimed that Sungai Chongkak is clean and
suitable as a recreational stream. Nevertheless, it
is very important to consider soil susceptibility
to erosion and protection of soil and water
resources in forest-based recreation (Maleknia et
al., 2013). In the meantime, a landscape master
plan should be prepared. It should be sensitive
to the environment, manage the recreational
forest to satisfy user needs, highlight
opportunities presently exist on site and the
necessary actions necessary to bring about the
level of recreation sought by the public.
In terms of design, it was found that Sungai
Chongkak applied medium designs (buildings
are not too huge and high) and portrays Malay
architecture (Figure 5). Malay architecture seems
to be more sensitive to local context and
environment, and can be applied to fulfil
ecotourism concept. Construction materials
selected for the park are largely of natural
materials like wood and clay bricks. These are
more in harmony with nature and did not pollute
the natural environment (Zucker et al., 1983).
The color applied to the accommodation
buildings portrays peacefulness and harmony
(Brenda & Robert, 1996) with surrounding
environment which is green and chocolate. It
does also create unity towards the environment
as well as influence users convenience (Arwed,
1992).
To maintain the aesthetic values of the park,
cleanliness, grass cutting, rubbish collection,
sweeping fallen leafs, toilets cleaning, bench
wipes and keeping the chalets tidy are normal
tasks that have been carried out. These efforts
reduce visual interference to the visitors such as
from rubbish mass, dirty walkways, roads
damages, and fallen trees. Furthermore, TSSB
has also done repairing and reconstruction works
for accommodation in ensuring users safety and
convenience as well as increasing their
experiences. Those activities have maintained
and enhance the aesthetic value of the park.
However, from field observation, there are some
elements that need to be repaired. For instance,
floor replacement for wooden bridge, repainting
and repairing works for wooden table and
cleaning the fallen leafs on the roof and wild
grasses on pedestrian walkways (Figure 6).
Figure 4: An ad hoc development approach of Sungai Chongkak Recreational Forest leading to
environment degradation.
Figure 5: Malay architecture applied in structure design in Sungai Chongkak Recreational Forest.
8 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
Figure 6: Some elements in Sungai Chongkak needs repairing and reconstruction works and wild grass on
pedestrian walkway need to be clean off.
From economic aspect, the author noticed
that the indirect benefits of the park are shared
with the local community as what Sungai Tekala
management had done. The management
allowed local people to run a small business in
and surrounding the park. This has helped the
local people to increase their socio-economy
through fruits, drinks, recreational essentials and
other agriculture products (e.g. papaya, petai,
tapioca, bananas and pineapple) selling.
However, that activity only benefits small
number of local residents. More effort need to
be carried on to increase the economic benefit of
the local people such as the management should
work with local tourism bodies to configure
recreation facilities to bring most added values to
the local economy and work with local
community groups who wish to develop
facilities, or offer franchises or agreements for
on-site infrastructures development.
In term of local participation, author noticed
that TSSB has taken a good step in involving the
locals into Sungai Chongkak Recreational Forest
landscape management system. There are seven
local people that have being appointed as general
workers. At the same time, several lots of
business space have been established in the park
to give opportunities for them to run business (as
food and souvenirs sellers). This has contributed
to positive economic growth of local peoples
directly or indirectly. However, local
community involvement should be increased by
appointed representatives among them in
management and invited them to attend meetings
related to Sungai Chongkak Recreational Forest
landscape development in the future. TSSB can
also make a memorandum of understanding
(MoU) with local people for homestay and
agrotourism projects surrounding the Sungai
Chongkak Recreational Forest. In fact, local
people who involved in managing natural
resources will be more compliant with the rules
that themselves have built over the rules imposed
on them by force (Wilshusen et al., 2003).
In term of governance, TSSB can be
considered as weak in landscape planning,
design, construction and maintenance. This is
because TSSB does not have any professionals
in those fields, but they have professionals in
tourism activity and marketing. Nevertheless,
TSSB has formed a collaboration activity with
Kajang Municipal Council (MPKJ), SFD and
Indah Water Consortium in construction works.
However, the collaboration exists only when it is
necessary (when a new accommodation/facility
wanted to be build) and not from the beginning
of the development process. These situations
happen because TSSB develop human made
landscape elements according to the necessity
and user’s need. Therefore, to make sure the
collaboration exist in a whole development
process, it is suggested that TSSB form special
work group that includes several experts namely
landscape architect, engineer, architect, forester
and product manager for their recreational
forests sites under supervision.
4.3 TEMPLER RECREATIONAL FOREST
Templer Recreational Forest is located at
coordinate 030 17'60" N 1010 39'25" E. Their
vegetations is a type of Lowland Dipterocarp
Forest. This recreation area is about 853
hectares. The area is bounded by the Ulu
Gombak Forest Reserve in the east, Serendah
Forest Reserve in the north and Kanching Forest
Reserve in the west (Gangadharan, 2005). In
October 1955, the government has allowed
Friends of Templer Park Society to manage the
park and they have been given MYR10,000.00
every year (Nadchatram, 1971). The society
managed the park until January 2002. Starting
February 2002, MPS takes over the management
until today (Gangadharan, 2005). MPS has a
plan to develop the Templer Recreational Forest
as a tourism site based on ecotourism concept
9 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
and recreational activity. Currently, MPS has
appointed consultant to prepare overall Templer
Park Landscape Master Plan. This step has been
taken since earlier management did not provide
any development plan including landscape
master plan for the area. The park is free to the
public.
Nowadays, the ecological integrity of
Templer Recreational Forest is being threatened
due to development pressure. Author noticed that
there are construction works in the vicinity of the
park such as housing development (bungalow
and high-end terrace house), road project and
golf courses. These have resulted in
deforestation, losing the rare and endemic forest
tree species such as Hopea subalata and impact
the streams quality in the park due to erosion.
Therefore, a close and thorough monitoring need
to be done by the management to make sure the
ecological stability of the park are not affected
seriously in the future.
During the field observation, it was found
that the designs of some landscape elements are
less in harmony with the surrounding
environment. This is especially true with an
element that has been built by the earlier
management. Those elements have been built on
an ad hoc and in situ basis, without any
suitability and environmental effects study
(Figure 7). It is recommended that the
management replace unsuitable materials used
earlier to a more harmony materials such as
natural stones. Meanwhile, new landscape
elements that has been built by MPS are looking
more eco-friendly and harmony with
surrounding environment such as wakaf and
public toilet (Figure 8). The architecture itself
portrays Malay architecture that enhances local
design with calm and peaceful colors (earth
colors). Materials used for construction which
are more resistant to the climate change were
made from concrete and clay bricks. The used of
wood as construction materials were reduced by
the MPS due to high maintanence. Furthermore,
footing system has been used for flood
protection and erosion especially near the river
bank and steepest area for certain elements.
Figure 7: Materials that have been used by earlier management before MPS take over such as marbles and
zinc are less harmony with surrounding environment and causes visual interference and it did not fulfil the
ecotourism concept.
Figure 8: New landscape elements that have been built by MPS are looking more eco-friendly and harmony
with surrounding environment such as wakaf and public toilet.
10 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
Figure 9: Some landscape elements in Templer Recreational Forest are unsafe to users and in bad
conditions due to landscape maintenance system weaknesses, no inspection and lack of budget.
Figure 10: Lacking supports from public to Templer Recreational Forest development could cause site
“abandonment”.
In ensuring the park aesthetic is in good
condition, cleanliness activity has been carried
out every day while repairing and reconstruction
works of structural elements such as toilet,
surau, shelter and others were carried out when
necessary. However, it was found that some of
the landscape elements in the park are in bad
conditions, unsafe to users and affecting the
beauty of the park (Figure 9). This situation
happens because there are some weaknesses in
maintenance system and no inspection tasks have
been taken to inspect the landscape elements
condition regularly as well as budget constraint.
Aesthetic of the park was also being threatened
by unsuitable developments like electric power
line across the park. Unsuitable materials used
such as marbles for park facilities also
contributed to the aesthetic value degradation.
Economically, Templer Recreational Forest
benefited the local residents. MPS has built
specific building for them inside the park to do
business like selling foods, drinks and snacks.
The author believed that in the future, local
people will receive more economic benefits due
to MPS planning to develop the park as one of
their tourism attraction. This effort indirectly
will attract more investors for ecotourism
activities in this recreational forest and attracting
more tourists to visit the park. In the meantime,
MPS did not impose any charge to the user, thus
they are free to use, enjoy and do recreation
activities that they like in the park. These
indirectly will reduce their burden to find a space
for outdoor activities for practicing healthy
lifestyle.
On the aspect of local participation, it was
found that the involvement was very low. MPS
involves them only as food and beverage sellers
at business space provided in the park, similar to
Sungai Chongkak and Sungai Tekala
Recreational Forest. Even though MPS claimed
that voices from the public (especially for those
who had business in the park before) has been
accounted, it did not represents the whole local
community voices. Previously, local
communities via Friends of Templer Park
Society was given a chance in managing the
area, but this permission was taken away
recently. This situation has resulted in the local
community perceiving that their involvement is
no longer needed. At the end, their supports to
Templer Recreational Forest development were
lower and could cause site “abandonment”. This
situation can be seen through the close proximity
11 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
to housing and village area, beside the main
roads, but the number of daily and weekend
visits from local people were very low. These
situations portray that local community ignore
the Templer Recreational Forest existence. If this
phenomenon continues, it will give some
difficulties to MPS to fulfil sustainable
development concept because of lower public
involvement.
Looking at the governance aspect, MPS has
a good management structure. MPS has enough
experts like landscape architects, architects,
engineers, planners, technical staffs and
administrators for managing the park. But, MPS
has failed to fully use their staffs in giving full
commitment and focus for Templer Recreational
Forest development. This can be seen where
there is no special groups formed among their
experts in discussing the park development.
Thus, there is a room for improvement especially
in benefitting the internal expects that MPS have.
Thus, it is suggested that MPS form experts’
team among their internal experts to gain
concrete ideas and full commitment for the
recreational forest. Through these expert groups,
planning and development of recreational forest
will be more efficient and effective as well as
reducing consultancy costs.
4.4 ANALYSIS TOWARDS SUSTAINABLE
LANDSCAPE DEVELOPMENT
Table 2 shows the results of analysis towards
sustainable landscape development of the study
sites. Analyses were focusing on landscape
ecology, economy, local participation,
governance, aesthetic and landscape designs
aspects which eventually need to be fulfilled by
respective management for achieving sustainable
landscape development of recreational forest.
Table 2: Analysis towards sustainable landscape development of the study sites
Sustainable
Aspects
Study Sites
Sungai Tekala Templer Sungai Chongkak
Landscape
Ecology
Maintained natural forest
from serious /major
damages
Established nursery plots
for educational purposes
Established demonstration
plots for forest
management educational
purposes
Has clean river and small
waterfall that are suitable
for water activities
Maintained existing
natural topography
Rich with faunas
Prepared overall
landscape master plan
Maintained existing
natural topography
Used eco-friendly
method in controlling
river bank erosion
Has waterfalls that is
in good condition that
portrays natural
environment
Forest vegetations in
virgin condition
Rich with faunas
Preserved natural forest
conditions from major
damages
Has bigger and linear flat
area for activities
Has clean river that is
suitable for water
activities
Forest vegetations in
virgin condition
Maintained existing
natural topography
Rich with faunas
Economy Provided business spaces
for small business
activities such as food and
beverage
Privatized rubbish
collection and cleanliness
activity
Developed the park as
recreational area
Provided business
spaces for small
business activities
such as food and
beverage
Privatized
construction and
reconstruction works
Developed the park
as recreational and
ecotourism area
Provided business spaces
for small business
activities such as food
and beverage
Appointed local peoples
as cleanliness staff
Privatized construction
and reconstruction works
Developed the park as
recreational and
ecotourism area
12 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
Local
Participation
Local participation
through business activities
Gets early opinions
from existing retailers
before new business
space will be build
Local participation
through business
activities
Allow existing aborigine
peoples in the park to
continue collect forest
products
Local participation
through business
activities
Governance Park was managed by
Recreational Forest and
State Park Unit, lead by
Forest Officer
Staffs expert in forest
management
Has initiative to have
collaboration with other
experts group via
consultancy
Park was managed by
Park and Recreation
Unit, lead by
Landscape Architect
Staff expert in
environmental design
and landscape
management
Organization has
experts group such as
landscape architect,
architect, planner and
engineer that are
suitable for
recreational forest
development
Has initiative to have
collaboration with
other experts group
via consultancy
Park was managed by
TSSB Product
Management Unit
Staffs expert in tourism
marketing
Has initiative to have
collaboration with other
experts group via
consultancy
Aesthetic Maintained forest
virginity for good
panoramic
Keep natural landscape in
good condition such as
waterfall and river
Has undulating
topography
Preserved interesting
undulating
topography including
seven natural
waterfalls
Preserved natural
stone hills for active
recreational activity
Has own historical
value due to it was
opened by British
colonial
Preserved natural forest
from major destruction
Has shallow and linear
river with a clean water
and natural rocks
River stones are nicely
arrange naturally
without human
disturbance
Designs Human made landscape
elements quite harmony
with existing environment
Enhanced Malay
architecture which is the
local design
Color scheme is harmony
with existing
environment
Use local materials such
as clay bricks and timber
Human made
landscape elements
quite harmony with
existing environment
Enhanced Malay
architecture which is
local design
Color scheme is
harmony with
existing environment
Use local materials
such as clay bricks
and timber
Human made landscape
elements quite harmony
with existing
environment
Enhanced Malay
architecture which is
local design
Color scheme is
harmony with existing
environment
Use local materials such
as clay bricks and
timber
13 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
Table 2 has shown that SFD compliance is
more on the aspect of ecological planning where
they managed natural forest in the park more
effectively which stressed on informal education
for visitors that can increase awareness among
the public. Furthermore, SFD is an experience
stakeholder in managing forest resources. On
the other hand, MPS complied more on the
aspect of good governance practice since it
encompass enough experts’ group in
implementing/practicing sustainable designs and
has collaboration with other outsource experts
via consultancy. For TSSB, their compliance is
more on increasing local peoples’ economy.
Many local people are being appointed as parts
of management staff and business opportunity
had been given to them.
The above analysis also shown that all
parties of respective recreational sites study need
to improve their planning development, increase
expert collaboration, involve more local people
in management process, improve landscape
maintenance system and programme, improve
landscape designs and control the number of
visitor. Most important thing is that the
management needs to understand that the design
concept of recreational forest should show the
uniqueness of forest, which differentiates urban
and natural design area. The design must put
higher concerns with the natural environment
through the understanding and adoption of the
"sense of place" and "genius loci" of the site
(Mohd Kher & Noorizan, 2006; Stephankova, et.
al., 2012). All responsible parties should also
seriously take into account the social, economic
and environmental aspects of ecotourism activity
that are being adopted on their site. This will
ensure a quality and sustainable recreational
forest landscape.
5. CONCLUSION
The sustainable development approach
implemented for the studies of recreational
forests in Selangor is good as it takes into
account the environment, social and economy. It
also stressed on unity and balance between
socio-economic development and environment
needs to fulfill current requirements without
affecting future needs. At the same time,
introducing recreational forest as ecotourism
destinations is in line with sustainable
development approach where it can educate
publics in understanding and learning about
forest environment, culture, landscape
appreciation, flora and fauna. Ecotourism is
expected to bring a minimal impact on the
environment as it stresses on environmental
conservation and the preservation of the local
community and culture. Ecotourism would also
bring economic benefits to local communities.
However, this study also shows that
recreational forest development in Selangor still
did not implemented sustainable landscape
development and thus need an improvement.
This lack of implementation was due to a
number of reasons including no proper planning,
low understanding of sustainable concept, lack of
staffs and insufficient supervision. If there are
no constructive actions taken to remedy the
situation, then the goal of sustainable
development cannot be achieved. Therefore,
several immediate actions need to be carried out.
These include encouraging staff to attend related
courses and seminars about sustainable
landscape development, increase the staff
numbers especially in landscape and built
environment field and focus on landscape
designs.
This study found that all study areas did not
have landscape development master plan. Most
of the development that has been implemented is
on an ad hoc basis and according to users’
demand. This has resulted in difficulty to create
recreational forest identity and fulfill sustainable
landscape development requirements. Human
made landscape elements were also designed
much like those in urban areas. A comprehensive
master plan for each recreational forest area is
necessary. The plan should focus on creating
identity and more accurate decision-making to
monitor the development process. This is very
important to achieve landscape sustainability for
recreational forests.
Recreational forest landscape development
must be planned before implementation to make
sure natural landscape resources (e.g. forest,
river, hill, waterfall, stones, etc.) continuously be
protected and preserved. It is also to make sure
that human made landscape elements can be in
harmony with existing environment. Thus,
infrastructure must conform to environment-
friendly, low-impact architecture; renewable
including solar energy, waste recycling,
rainwater harvesting, natural cross-ventilation,
no use of asbestos, controlled sewage disposal,
and merging with the surrounding landscape.
14 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
The design should enhance local architecture,
use local materials as well as portrays local art
and culture.
Finally, cooperation from all parties and
stakeholders are needed in ensuring sustainable
landscape development of recreational forest in
Selangor towards forest sustainability. All levels
of public including politician, professionals,
supporting groups, local community and
recreational forest users should play their own
role in ensuring landscape sustainability.
Development process of recreational forest
landscape must start from down to top levels
from user level, local community, owner,
political and decision makers. In line with this,
overall recreational forest landscape master plan
is very important to be prepared to make their
development more effective and efficient. It is
also to make sure sustainable landscape
development principles being fulfill by the
management. Once it has become a reality, our
forest will be more sustainable and abandon
situation can being avoided for the benefits of
future generation.
6. ACKNOWLEDGEMENT
This study acknowledged the Selangor Forestry
Department for the information’s provided and
Sg. Chongkak, Sg. Tekala and Templer
Recreational Forest management for the
information provided, as well as allowing author
to carry out study in their parks. Special thanks
also go to Associate Professor Dr. Robert Kabai
for the supervision and Professor LAr. Dr.
Mustafa Kamal Mohd Shariff for editing the
manuscript.
7. REFERENCES
Arwed, T. (1992). Ecologis planning.
Braunschweig, Wiesbaden: Fried,
Vieweg & Son.
Botes, L., & Rensburg, D. V. (2000).
Community participation in
development - Nine plaques and twelve
commandents. Community Development
Journal, 35(1), 41-58.
Brenda. V., & Robert, V. (1996). Green
architecture: Design for a sustainable
future. London: Thames and Hudson
Ltd.
Buchecker, M., Hunziker, M., & Kienast, F.
(2003). Participatory landscape
development - Overcoming social
barriers to public involvement.
Landscape and Urban Planning, 64, 29-
46.
Ceballos-Lascurain, H. (1996). Tourism,
ecotourism and protected areas - The
state of nature-based tourism around
the world and guidelines for its
development. Gland, Switzerland and
Cambridge, UK: IUCN.
Chee, T.Y. (1986). Forest recreation
development in Peninsular Malaysia.
Paper presented in the 9th Persidangan
Perhutanan Malaysia. Forestry
Department Head Quarter, Kuala
Lumpur, Malaysia.
Clark, WC., & Dickson, N.M. (2003).
Sustainability science - The emerging
research program. Proceedings of the
National Academics of Science of the
United States of America. 100:8059-
8061. Retrieved from,
http://www.pnas.org/content/100/14/80
59.full.
Collins, K., Blackmore, C., Morris, D., &
Watson, D. (2007). A systematic
approach to managing multiple
perspectives and stakeholding in water
catchments: Some findings from three
UK case studies. Environmental Science
and Policy, 10(6), 564–574.
Doczi, G. (1994). The power of limits -
Proportional harmonies in nature, art
and architecture. Boston, London:
Shambala.
Dunnett, N., & Clayden, A. (2007). Resources -
The raw materials of landscape. In
J.Benson & M. Roe (Eds.), Landscape
and Sustainability (2nd ed), (196-221).
London: Routledge.
Farina, A. (2006). Principles and methods in
landscape ecology - Towards a science
of the landscape (2nd ed.) Dordrecht:
Springer.
Foresty Department Peninsular Malaysia. (2007).
Forestry statistics Peninsular Malaysia.
Kuala Lumpur, Malaysia.
Gangadharan, N. (2005). Templer Park - Pages
from the past. Selangor, Malaysia:
Pelanduk Publications (M) Sdn Bhd.
GLP. (2005). Science plan and implementation
strategy. IGBP Report No. 53/IHDP
Report No. 19. IGBP secretariat,
Stockholm.
Gobster, PH. (2008). Yellowstone hotspot -
Reflections on scenic beauty, ecology,
and the aesthetic experience of
15 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
landscape. Landscape Journal, 27, 2-
08.
Gobster, P.H., Nassauer, J.I., Daniel T.C., & Fry,
G. (2007). The shared landscape -
What does aesthetics have to do with
ecology? Landscape Ecology, 22, 959–
972.
Haines-Young, R., Watkins, C., Wale, C., &
Murdock, A. (2006). Modelling natural
capital - The case of landscape
restoration on the South Downs,
England. Landscape and Urban
Planning, 75(3–4), 244–264.
Hamilton, K., & Selman, P. (2005). The
‘landscape scale” in planning - Recent
experience of biogeographic planning
units in Britain. Landscape Research
30(4), 549-558.
Ismail, S., & Mohd Sarofil, A.B. (2005).
Landscape for children to play and learn
- A conceptual comparison between
natural stream and playground. Jurnal
Teknologi, 42(B), 1–10.
Jacobs, A.B. (1993). Great Streets.
Massachusetts: MIT Pres.
Jamieson, W., & Noble. A. (2000). A manual for
sustainable tourism destination
management. CUC-UEM project, AIT.
Retrieved from, http://www.ecoindia.
com/sustainable-tourism.html.
Kates, R.W., Clark, W.C., Corell, R., Hall, J.M.,
Jaeger, C.C., Lowe, I., McCarthy, J.J.,
Schellnhuber, H.J., Bolin, B., Dickson,
N.M., Faucheux, S., Gallopin, G.C.,
Grubler, A., Huntley, B., Jager, J.,
Jodha, N.S., Kasperson, R.E.,
Mabogunje, A., Maston, P., Mooney,
H., Moore III, B., O’Riordan, T., &
Svedin, U. (2001). Sustainability
Science. Science, 292(5517), 641-642.
Lee, T. (1976). Psychology and the
Environment. London: Methuen.
Maleknia, R., Mirarb, J., Moghaddam, M.N., &
Shahrali, A. (2013). An ecological
capability evaluation model for
recreation, conservation and protection
functions of Iran’s Zagros. International
Journal of Agriculture: Research and
Review, 3(2), 458-466.
Mohd Kher, H. (2012). Persepsi pihak
berkepentingan terhadap pembangunan
dan pengurusan landskap hutan
rekreasi di Selangor, Malaysia.
(Unpublished PhD. Thesis). Universiti
Kebangsaan Malaysia: Bangi, Malaysia.
Mohd Kher, H., & Noorizan, M. (2006). A study
on visual quality of tourism
accomodation in eco-tourism site in
Paya Indah Wetlands, Malaysia. Asean
Journal on Hospitality and Tourism,
5(2), 103-116.
Mohd Yazid, M. Y. (2009). Using planning for
real method in the redesign of the
neighbourhood park - Community
participation in Datuk Keramat Lake
Garden, Kuala Lumpur. (Unpublished
PhD thesis). University of Newcastle
upon Tyne: United Kingdom.
Mustaqim-Alias, M., & Ahmad, A.K. (2013).
Benthic macroinvertebrates diversity
and water quality assessment at Sungai
Chongkak recreational area, Hulu
Langat, Selangor. Academic Journal,
1571, 608.
Nadchatram, N. (1971). A guide to Taman
Rimba Templer (Templer Park).
Malayan Nature Journal, 24(3 & 4).
Nicol, C., & Blake, R. (2000). Classification
and use of open space in the context of
increasing urban capacity. Planning
Practice and Research, 15(3), 193-210.
NRC. (1999). Our common journey - A
transition toward sustainability. A
Report of the Board on Sustainable
Development of the National Research
Council. National Academy Press:
Washington, D.C.
Osman, M.T. (2005). Urban landscape
management in Malaysia - In search of
a sustainable management system.
(Unpublished. PhD Thesis). University
of Newcastle upon Tyne: United
Kingdom.
Powell, J., Selman, P., & Wragg, A. (2002).
Protected areas - Reinforcing the
virtuous circle. Planning Practice and
Research, 17(3), 279–295.
Rametsteiner, E. (2007). Improving governance
for SFM at local and regional levels. In
United Nations forum on forest,
Enabling sustainable forest
management: Strategies for equitable
development, for forests, for people.
New York, USA: United Nations.
Schmid, P. (1983). Bio-logis architectur (2nd
ed.). Koln-Braunsfeld: Rudolf Muller.
Schneider, R. (1981). Natural building.
Stuttgart: Institut fur leichten Flachen
tragwerke.
Schutzki, R., & Tripp, E. (2007). Sustainable
approaches to the conventional
16 Journal of Design and Built Environment Vol. 14 (2), December 2014 Mohd Kher, H.
landscape. Paper presented at 2nd
Annual Meeting and Professional
Improvement Conference. Grand
Rapids, Michigan: National Association
of County Agricultural Agents.
Selman, P. (2008). What do we mean by
"sustainable landscape"? Sustainability:
Science, Practice, & Policy 4(2), 23-28.
Retrieved from, http://ejournal.nbii.
org/archives/vol4iss2/communityessay.s
elman.html.
Soy, S.K. (1997). The case study as a research
method. (Unpublished paper).
University of Texas at Austin, Texas.
Stephankova, R., Bihunova, M., & Kabai, R.
(2012). Design principles of public and
recreational areas in the urban
environment. Slovakia: Slovak
University of Agriculture.
Stouter, P. (2008). Shaping buildings for the
humid tropics: Cultures, climate and
materials. Retrieved from,
www.earthbagbuilding.com.
Szerletics, A. (2011). The role of good
governance practices in the protection
of fundamental rights. Pro Publico
Bono Online Tamop Special 2011.
Retrieved from,
http://www.propublicobono.hu/pdf/Szer
letics_A_Good_governance[1].pdf
Tàbara, J., & Pahl-Wostl, C. (2007).
Sustainability learning in natural
resource use and management. Ecology
and Society, 12(2), 3. Retrieved from,
http://www.ecologyandsociety.org/vol1
2/iss2/art3/.
Turner, B.L.I. (2008). Sustainable land
architecture – Directions in land
change science. In 4th IGBP Congress
Sustainable Livelihoods in a Changing
Earth System, Working Group Session
C6/D6, Grand Challenges for Land
Systems and Sustainability Science; and
Land System Change - Competing for
Food, Energy and Environment
Services, Cape Town, South Africa.
Vollet, D., Candau, J., Ginelli, L., Michelin, Y.,
Menadier, L., Rapey, H., & Dobremez,
L. (2008). Landscape elements - Can
they help in selling “protected
designation of origin” products?
Landscape Research, 33(3), 365–384.
Walter, G. (1987). Design in Architecture.
Koln: Rudolf muler.
Wilshusen, P.R., Brechin, S.R., Fortwangler,
C.L., & West, P.C. (2003).
Conservation and development at the
turn of the twenty-first century. In, S.R.
Brechin., P.R. Wilshusen., C.L/
Fortwangler., & P.C. West. (Eds.),
Contested nature: Promoting
international biodiversity with social
justice in the twenty-first century, (pp.1-
22). State University of New York:
Albany, NY.
Zucker, W.M, Hochberg, J., Tyng, A.G., Cass,
G., & Senkenitch, A. Jr. (1983). The
image and imagination of the architect.
In A.G. Read., P.C. Doo., & J. Burton
(Eds.), Architecture and Visual
Perception. Cambridge: MT Press.